Method for Determining 11 Perfluorinated Compounds in Quartz Sand and Soil Using Anyeep TQ9120

This study utilized the Anyeep TQ9120 ultra-high-performance liquid chromatography-tandem mass spectrometry system from AnyiPu to develop a method for the simultaneous detection of 11 per- and polyfluoroalkyl substances (PFAS) in quartz sand and soil. The method demonstrated excellent linearity, with limits of detection and quantification meeting relevant regulatory standards. Using this method and equipment enables reliable detection and quantification of PFAS.
Per- and polyfluoroalkyl substances (PFAS) are a class of synthetic persistent organic pollutants characterized by stable carbon-fluorine bonds that resist natural degradation. They exhibit long-range transport potential and bioaccumulation tendencies. Soil and sediment serve as their primary environmental sinks, acting as key vectors for PFAS entry into ecological cycles. Their contamination levels directly impact ecosystem safety and human health, making the monitoring and control of PFAS in soil and sediment a critical focus of environmental surveillance.
This study covers sample types including soil (agricultural, industrial vicinity, urban green spaces, background areas) and sediment (riverbeds, lake bottoms, marine sediments). To standardize testing procedures and ensure data accuracy and compliance, all tests strictly follow current Chinese standards, such as T/ZJEEMA XXXX-2024 "Determination of 20 Per- and Polyfluoroalkyl Substances in Soil by Liquid Chromatography-Tandem Mass Spectrometry." This method provides a scientifically reliable technical basis for pollution surveys, risk assessments, and management of PFCs in soil and sediment. This method is adapted fromHJ 1334-2023Quantified using the internal standard method.
Instruments and Reagents
Anyeep TQ120 Ultra-High Performance Liquid Chromatography-Tandem Mass SpectrometrySystem
Methanol(MS grade, ANPEL Shanghai)
Ammonium acetate (HPLC grade,Shanghai ANPEL)
Ammonia (Analytical Reagent,Shanghai ANPEL)
Acetic Acid (Analytical Reagent,Shanghai ANPEL)
Liquid Chromatography Conditions
Mobile PhaseA: 5 mM ammonium acetate–water
Mobile Phase B: Methanol
Chromatography column: Waters ACQUITY UPLC BEH C18 1.7μm, 2.1*100 mm
Column Temperature:40 ℃
Flow rate: 0.3 mL/min
Injection volume:5 μL
Mass Spectrometry Conditions
Ionization Source: Electrospray Ionization Source (ESI)-)
Source Temperature: 550 ℃
Spray Voltage: 4500 V
air curtain: 40 psi
Mist gas: 60 psi
Auxiliary Gas: 60 psi
Crash: 10
Scan Mode:MRM
Gradient elution program
Time min | A% | B% | Flow Rate mL/min |
0 | 80 | 20 | 0.3 |
3 | 40 | 60 | 0.3 |
7 | 30 | 70 | 0.3 |
9 | 20 | 80 | 0.3 |
9.1 | 2 | 98 | 0.3 |
10 | 2 | 98 | 0.3 |
10.1 | 80 | 20 | 0.3 |
13 | 80 | 20 | 0.3 |
Analyte MRM Parameters
No. | Test Item | Q1 Ion | Q3 Ion | CE (V) | DP (V) | Retention Time |
(min) | ||||||
1 | PFBA-1 | 212.9 | 168.8* | 2 | 40 | 3.1 |
| PFBA-2 | 212.9 | 96.8 | 10 | 40 | 3.1 |
2 | PFPA-1 | 263.0 | 219.0* | 4 | 30 | 4.2 |
| PFPA-2 | 263.0 | 69.0 | 4 | 30 | 4.2 |
3 | PFHxA-1 | 313.1 | 269.0* | 1 | 20 | 5.0 |
| PFHxA-2 | 313.1 | 119.0 | 15 | 20 | 5.0 |
4 | PFHpA-1 | 363.0 | 169.0* | 10 | 40 | 5.9 |
| PFHpA-2 | 363.0 | 119.0 | 14 | 40 | 5.9 |
5 | PFOA-1 | 413.0 | 369.0* | 12 | 30 | 7.1 |
| PFOA-2 | 413.0 | 169.0 | 2 | 30 | 7.1 |
6 | PFNA-1 | 463.0 | 419.0* | 14 | 30 | 8.5 |
| PFNA-2 | 463.0 | 169.0 | 2 | 30 | 8.5 |
7 | PFDA-1 | 513.0 | 469.0* | 14 | 30 | 9.6 |
| PFDA-2 | 513.0 | 219.0 | 5 | 30 | 9.6 |
8 | PFBS-1 | 299.0 | 80.0* | 56 | 90 | 4.3 |
| PFBS-2 | 299.0 | 99.0 | 68 | 90 | 4.3 |
9 | PFHxS-1 | 398.9 | 80.0* | 70 | 40 | 6.0 |
| PFHxS-2 | 398.9 | 99.0 | 50 | 40 | 6.0 |
10 | PFHpS-1 | 448.9 | 80.0* | 70 | 40 | 7.2 |
| PFHpS-2 | 448.9 | 99.0 | 60 | 40 | 7.2 |
11 | PFOS-1 | 499.0 | 80.0* | 68 | 150 | 8.5 |
| PFOS-2 | 499.0 | 99.0 | 80 | 150 | 8.5 |
12 | PFHxA-13C2 | 315.0 | 270.0 | 0 | 30 | 5.0 |
13 | PFOA-13C4 | 417.0 | 372.0 | 12 | 30 | 7.1 |
14 | PFOS-13C4 | 503.0 | 80.0 | 68 | 150 | 8.5 |
Note: * indicates the quantification ion pair.
Sample Processing
Sample ProcessingWeigh approximately 2 g of the sample (accurate to ±0.01 g) and add 20.μMix the internal standard intermediate solution with 10 mL of methanol-water mixture, vortex for 1 min, and oscillate at 300 r/min at room temperature for 2 h using an extraction device. Centrifuge for 10 min. Transfer the supernatant to another centrifuge tube, add 10 mL of methanol-water mixture to the original tube containing the sample, and repeat extraction 1 times. Combine all 2 extracts. Process the combined extract through 0.8. μAdd 80 mL of water to the filtrate from the syringe filter. Adjust the pH to 6-8 using acetic acid or ammonium hydroxide, then proceed with purification.
Activate the solid-phase extraction (SPE) cartridge sequentially with 6 mL ammonia-methanol mixture, 6 mL methanol, and 6 mL water. Pass the diluted extract through the SPE cartridge at a flow rate of 3-5 mL/min. Rinse the cartridge sequentially with 6 mL water and 8 mL ammonium acetate buffer; discard the rinse fractions. Elute the cartridge with 8 mL methanol at a flow rate of 1-3 mL/min and discard the eluate. Finally, elute the cartridge with 6 mL ammonia-methanol mixture at a flow rate of 1-3 mL/min, collecting the eluate in a centrifuge tube. Concentrate the eluate to near dryness, reconstitute with methanol to a final volume of 1 mL, and mix well before 0.22. μFilter the sample using a syringe filter into an injection vial for analysis.
Standard Curve PreparationAccurately pipette the appropriate amount of mixed standard working solution and mixed internal standard working solution, then dilute with volumetric solution to0.05 μg/L,0.1 μg/L,0.2 μg/L,0.5 μg/L, 1 μg/L, 2 μg/L, 5 μg/L, 10 μg/L, 20 μg/L, 50 μg/L、100μg/L series standard solutions for determination by liquid chromatography-tandem mass spectrometry (LC-MS/MS).
Linear Range
No. | Test Item | Retention Time min | Limit of Detection μg/kg | Limit of Quantitation μg/kg | Linear Range ng/mL | Linear Equation 1/x2 weighted | correlation coefficient r2 |
1 | PFBA | 3.096 | 0.01 | 0.025 | 0.05-100 | Y = 0.468295 * X + 0.00552693 | 0.9953 |
2 | PFPA | 4.187 | 0.01 | 0.025 | 0.05-100 | Y = 0.699434 * X + 0.00195754 | 0.9950 |
3 | PFBS | 4.327 | 0.002 | 0.005 | 0.05-100 | Y = 0.635977 * X + 0.00200498 | 0.9943 |
4 | PFHxA | 4.946 | 0.002 | 0.005 | 0.05-100 | Y = 0.183649 * X + 0.00890017 | 0.9988 |
5 | PFHpA | 5.935 | 0.01 | 0.02 | 0.05-100 | Y = 0.0144519 * X + 0.000636203 | 0.9942 |
6 | PFHxS | 6.004 | 0.0015 | 0.004 | 0.05-100 | Y = 0.720398 × X - 0.0030657 | 0.9941 |
7 | PFOA | 7.140 | 0.005 | 0.02 | 0.05-100 | Y = 0.138985 * X + 0.00355667 | 0.9977 |
8 | PFHpS | 7.209 | 0.0025 | 0.0075 | 0.05-100 | Y = 0.521476 * X + 0.000325136 | 0.9917 |
9 | PFNA | 8.483 | 0.005 | 0.015 | 0.05-100 | Y = 0.0832714 * X + 0.000761305 | 0.9944 |
10 | PFOS | 8.523 | 0.005 | 0.01 | 0.05-100 | Y = 0.297214 * X + 0.00201583 | 0.9939 |
11 | FDA | 9.571 | 0.005 | 0.01 | 0.05-100 | Y = 0.117769 * X + 0.00235339 | 0.9906 |
Summary
This study established a UHPLC-MS/MS method using the Anyeep TQ9120 for the analysis of 11 perfluorinated compounds. Results demonstrate that the method offers excellent sensitivity, stability, and linear range, making it suitable for routine analysis and detection of perfluorinated compounds.